• Tidak ada hasil yang ditemukan

View of Physiological and Biochemical Responses to Aluminum Stress in the Root of a Biodiesel Plant Jatropha curcas L.

N/A
N/A
Protected

Academic year: 2023

Membagikan "View of Physiological and Biochemical Responses to Aluminum Stress in the Root of a Biodiesel Plant Jatropha curcas L."

Copied!
7
0
0

Teks penuh

(1)

Vol. 19 No. 1, p 37-43 EISSN: 2086-4094

http://journal.ipb.ac.id/index.php/hayati DOI: 10.4308/hjb.19.1.

Physiological and Biochemical Responses to Aluminum Stress in the Root of a Biodiesel Plant Jatropha curcas L.

RADITE TISTAMA1,2, UTUT WIDYASTUTI1,2, DIDY SOPANDIE3, AKIHO YOKOTA4, KINYA AKASHI4, SUHARSONO1,2∗∗∗∗∗

1Department of Biology, Faculty of Mathemathics and Natural Sciences, Bogor Agriculture University, Darmaga Campus, Bogor 16680, Indonesia

2Research Center for Bioresources and Biotechnology, Bogor Agricultural University, Darmaga Campus, Bogor 16680, Indonesia

3Department of Agronomy and Horticulture, Faculty of Agricultural, Bogor Agricultural University, Darmaga Campus, Bogor 16680, Indonesia

4Nara Institute for Science and Technology, 8916-5 Takayama, Ikoma, NARA 630-0192, Japan

Received October 27, 2011/Accepted March 26, 2012

We investigated J. curcas responses to aluminum stress, histochemically and biochemically. Histochemical stainings were observed to analysis aluminum accumulation, lipid peroxidation and the loss of plasma membrane integrity on the surface and tissue of the root apex. Enzymatic analysis was conducted to measure malate content in leaf, root and malate efflux in the medium. We used M. malabathricum as a comparison for Al-tolerance plant.

J. curcas root elongation was inhibited by 0.4 mM AlCl3, while M. malabathricum root elongation was inhibited by 0.8 mM AlCl3 treatment. Inhibition of root elongation has high correlation with Al accumulation in the root apex, which caused lipid degradation and cell death. Generally, malate content in J. curcas leaf and root was higher than that in M. malabathricum. In the contrary malate efflux from the root into the medium was lower. J. curcas root has a different pattern compared to M. malabathricum in malate synthesis and malate secretion when treated with a different Al concentration. We categorized J. curcas acc IP3 as more sensitive to aluminum than M. malabathricum.

Key words: Jatropha curcas, aluminum stress, malate content

___________________________________________________________________________

_________________

∗∗∗∗∗Corresponding author. Phone: +62-251-8621257,

Fax: +62-251-8621724, E-mail: [email protected]

INTRODUCTION

Due to severe energy crisis and escalation of petroleum price, alternate energy sources are gaining importance (Ragauskas et al. 2006). One alternative energy source available is J. curcas seed oil. J. curcas is easy to propagate, has a high content oil seed, a short gestation period, rapid growth, and can be adopted into a wide variety of agro-climatic condition (Divacara et al. 2010).

Nevertheless, J. curcasshould not be cultured in large scale fertile soil. These lands should be allocated for more valuable food-crops. The alternative area for J. curcas plantation is the marginal areas, for examples some part of Sumatra Island and Kalimantan Island, which have acidic soil with Al toxicity as a major problem.

Al toxicity mostly affects root growth inhibition of Al- treated plants (Nagy et al. 2004), and also reduces root/

shoot biomass (Poschenrieder et al. 2008), and in the long term, of course, it will affect crop yield. Pisum sativum treated with aluminum show various responses to Al stress such as root growth inhibition, Al accumulation, lipid peroxidation, and loss plasma membrane integrity (Yamamoto et al. 2001). Reactive oxygen species (ROS)

appears to be the primary factors that cause growth inhibition in Al-stressed roots (Yin et al. 2010).

Several methods have been developed to identify mechanism of aluminum toxicity in root. The staining of Al-stressed root apices using hematoxylin appears to be a powerful tool to assist in Al-tolerance selection in plant breeding programs (Cançado et al. 1999). Localization of Al in the root could be rapidly observed using whole root or anatomy section (Yamamoto et al. 2001; Tamas et al.

2006). The lipid peroxidation is a relatively early symptom induced by the accumulation of aluminum (Yamamoto et al. 2001), and it increases with increasing Al concentration (Achary et al. 2008). Peroxidation of lipid can be detected by Schiff’s reagent staining (Yamamoto et al. 2001), which detect peroxide-derived aldehydes, formed downstream of reactive oxygen species (Yin et al. 2010). The late biological symptom of Al toxicity is the loss of plasma membrane integrity which causes the inhibition of root elongation (Yamamoto et al. 2001). The loss of plasma membrane integrity affect the viability of cells which could be determined by Evan’s blue staining (Tamas et al. 2006).

Organic acids with Al-chelating ability play a role in detoxification, externally and internally (Ma et al. 2000).

Exudation of organic acid such as citrate, malate and oxalate into the rhizosphere has been proposed as tolerance mechanism to avoid Al toxicity in many plants

(2)

(Ryan et al. 1995). Al stimulates citrate, malate, and succinate efflux from intact roots, but citrate release exhibited greatest Al-induced respond (Osawa & Kojima 2006). The organic acid in rhizosphere may chelate Al outside the membrane plasma, thereby preventing its uptake (Miyasaka et al. 1991). In vitro, organic acids do indeed decrease Al toxicity; citrate is more effective than succinate and malate (Hue et al. 1986). Tolerance varieties of Oriza sativa, have higher citrate synthesis than in those of sensitive varieties (Kang & Ishii 2006). Citrate chelates Al and makes an Al-citrate complex that is not phytotoxic (Ma 2000). Also, citrate has been shown previously to enhance the availability of phosphorus (P) from insoluble Al phosphates (Miyasaka et al. 1991). In wheat (Triticum aestivum L.), Al-tolerance seedling secreted malate four times higher than Al-sensitive seedling after a 2-h exposure to 200 μM Al (Delhaize et al. 1993).

Overexpression of enzymes involved in organic acid metabolism citrate synthase in transgenic tobacco, Arabidopsis, and alfalfa (De la Fuente et al. 1997), and Daucus carota L. (Koyama et al. 1999) can, in some cases, result in increased root organic acid content and exudation, as well as enhanced Al tolerance. Expression of ALMT1, a malate transporter that is associated with malate efflux and Al tolerance in Al- sensitive barley can increased malate efflux with properties similar to those of Al- tolerance wheat (Delhaiez et al. 2004).

The response of J. curcas to aluminum stress is not yet observed in detail. An understanding of Al toxicity and mechanism of tolerance is important to develop future breeding and cultivation protocol in J. curcas. The objective of this study is to confirm physiological and biochemical characteristic of J. curcas under Al stress condition.

MATERIALS AND METHODS

Jatropha curcas variety IP-3 was used for our experiment. Seeds were submerged with tap water for 1 hour and then sterilized with Na hypochlorite solution (1 ml Na hypochlorite, 10 ml Tween-20, and 20 ml water) for 10 minutes. After rinsed with sterile water, the seeds were grown in isolite for 10 days. High vigour of seedlings was selected for Al treatment in hydroponic culture containing half strength of Murashige and Skoog (MS) medium (1962). An Al-tolerant species, Melastoma malabathricum, was used as a comparison plant. M. malabathricum seedlings were grown in the soil for 1 month, and transferred to hydroponic medium pH 5.8 for a week before treated with different Al concentration.

Root Growth Inhibition. The ten-day old J. curcas seedling were treated with different concentrations (0, 0.2, 0.4, and 0.8 mM AlCl3) in the half strength of MS medium, and adjusted at pH 4 for 7 days. Each treatment consisted of five seedlings with four replicates. The media were renewed with fresh media on the fourth day. All lengths of the primer roots were measured with a ruler before treatment and after treatment.

Al Accumulation. To determine histological and physiological aspect, we used two Al-treatments with and without 0.8 mM AlCl3 for 7days in hydroponic culture.

The longest root of a seedling was rinsed extensively in distilled water for 1 hour, and submerged in a solution consisting of hematoxylin staining [0.2% w/v hematoxylin in 0.02% (w/v) KIO3] for 10 minutes. The roots were then washed with repeated changes of distilled water for 1 hour, and evaluated for the degree of hematoxylin staining in the root tips. The root tips staining pattern were photographed with a photomicroscope (Tamas et al. 2006).

The transversal sections of the first cm of the root apex were prepared with free hand section.

Injury of Plasma Membrane. Injury of plasma membrane by several reactive oxygen species were detected using Schiff’s reagent (Yamamoto et al. 2001).

The roots were submerged in Schiff’s reagent for 10 min, and rinsed with 0.5% (w/v) K2S2O5 in 0.05 M HCl. The stained roots were kept in sulphite solution to retain the staining color. The stained roots were observed under a light microscope.

The Localization of the Loss of Plasma Membrane Integrity. The roots were submerged in 10 ml of Evan’s Blue solution [0.025% (w/v) Evans blue in 100 mM CaCl2, pH 5.6] for 10 min. The stained roots were then washed three times with 200 ml of 100 mM CaCl2 (pH 5.6). The root tips were observed under a light microscope.

Organic Acid Content in the Root, Leaves and Media.

Organic acid extraction followed the method described by Delhaize et al. (1993). Roots and fully opened leaves were washed gently to remove salt and blotted dry with paper towels. About 0.3-0.5 g of the first cm of root tips and leaf were collected from 10 mm length root tips, frozen in liquid nitrogen, and stored at -80 oC until extracted. The samples were grounded by mortar and pestle in the presence of liquid nitrogen, and added 1 ml of 0.6 N perchloric acid and then grounded further. The extract was transferred to a 1.5 ml plastic tube, centrifuged at 15,000 g for 5 minutes, then 0.9 ml of the supernatant was collected to a new plastic tube. The supernatant was neutralized by adding 80 ml of K2CO3 (69 g/100 ml). The neutralized solution was centrifuged at 15,000 rpm for 5 minutes. For malic acid assay, 0.25 ml of the sample was incubated with 0.75 ml of buffer (0.5 M glycine, 0.4 M hydrazine, pH 9.0), and 0.05 ml of 40 mM NAD. The reaction mixture was pre-incubated for 30 minutes to obtain a stable A340 reading before the addition of 5 μl of malate dehydrogenase. The increase in A340 was equal with the production of NADH and directly proportional with amount of malic acid content in the sample (Delhaize et al.

1993).

RESULTS

Root Growth Inhibition. After the 7th day cultured in nutrient containing differential Al level, the growth of primary roots were reduced. At the level Al was 0.2 mM, the root growth were not significantly inhibited compared

(3)

to roots without Al treatment, but when the Al level was increased to 0.4 and 0.8 mM Al, J. curcas showed 36.17 and 48.02% inhibition of root elongation, respectively (Figure 1a). The negative effect of Al did not occur in the Al tolerance plant, M. malabathricum. Al treatment of 0.4 mM had a positive effect on M. malabathricum root growth while adding 0.8 mM of Al also did not reduced its root elongation (Figure 1b).

Al Accumulation. By using hematoxylin staining, Al accumulation was detected in the J. curcas roots. The Al accumulation was intensively localized in the first cm of the root tip; where the upper region of the first cm of the root tip saw a significant decrease in Al accumulation (Figure 2a). Hematoxylin staining of transversal section at the first cm of the root apex was intensive in almost all of the root tissue; the epiderm and the cortical cell wall were penetrated as well as the endoderm, xylem and phloem (Figure 2d). In the M. malabathricum root tip treated with 0.8 mM Al, the hematoxylin staining was colorless for the entire root surface (Figure 2g).

Injury of Plasma Membrane. After grown in the nutrient solution containing 0.8 mM Al for seven days and then stained with Schiff‘s reagent, the J. curcas root was clearly pink and homogenous in the first cm root apex, which represented aluminum distribution (Figure 2b).

Transversal section view of the root treated with Al also showed a clear pink color for the entire root tissue, mainly around the epiderm and cortext (Figure 2e). Schiff’s reagent staining didn’t show in M. malabathricum root apex (Figure 2h).

The Localization of the Loss of Plasma Membrane Integrity. Blue dye around the J. curcas root apex showed that extensive loss plasma membrane integrity was induced by Al treatment (Figure 2c). Evans blue staining was intensively obtained at the first cm of the root tip surface and by the transverse section, the infiltration of the Evan Blue dye occured in all parts of the root tissue (Figure 2f).

There was no blue color in the root apex surface of

M. malabathricum after treated with 0.8 mM Al for 7days (Figure 2j).

Organic Acid Content in the Root, Leaves and Media.

Malate content in the J. curcas leaf without aluminum stress was fifteen times higher than that of M.

malabatrichum, and the content was 61.7 μmol g-1 FW (24.6%) down by increasing Al concentration. Without Al stress, the malate content in M. malabathricum leaf was 16.74 μmol g-1 FW and decreased by 46.44% for 0.2 mM of Al stress. It was stable when Al stress was increased (Figure 3a,b).

Without Al stress, malate content in J. curcas root was 24.56 μmol g-1 FW, or 2.78 times higher than that of M. malabathricum root. The respond of root apex to Al stress in J. curcas and M. malabathricum was quite different, where Al-induced malate in the J. curcas root was significantly increased (66.01 μmol g-1 FW) in 0.8 mM Al stress for 7 days, while in the M. malabatrichum root, the Al-induced malate reached peak (19.6 μmol g-1 FW) at 0.4 mM Al treatment, and tended to decrease in 0.8 mM Al stress (Figure 3c,d).

Both J. curcas and M. malabathricum secreted malate to the medium without Al stress, each 0.102 and 0.174 μmol g-1 FW, respectively. The peak of malate exudation in J. curcas root occurred at 0.4 mM AlCl3 treatment (0.357 μmol g-1 FW) and then significantly decreased under 0.8 mM AlCl3 treatment. In M.

malabathricum root, the highest number of malate exudation occurred at 0.8 mM AlCl3 treatment (0.466 μmol g-1 FW) (Figure 3e,f).

DISCUSSION

Aluminum inhibits J. curcas root elongation in a relative high concentration, more than 0.2 mM. In other sensitive species, such as Triticum aestivum variety Scout 66 (Ma et al. 2004; Leucaena leucocephala (Osawa &

Kojima 2006), exposure to 10 mM Al, significantly inhibited

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatment

Root elongation (cm/week)

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatment

Root elongation (cm/week)

Figure 1. Effect of Al concentration on root elongation of J.curcas (a) and M. malabathricum (b) after growed on the nutrient culture for 7days in 250 ml of nutrient solution that contained various concentration of Al. The error bars denote the SE values of the mean of ten seedlings.

a b

a

abc

bc

c

b b

a

b

(4)

(about 40% inhibition) the root elongation. Some paper reported to only use Al concentration less than 0.2 mM to categorize whether the plants were categorized as Al sensitive or tolerant (Silva et al. 2010). In Al-tolerance Picea abies, the root growth decreased about 40% after treated with 0.5 mM Al for 2 days (Nagy et al. 2004), while in several Eucaliptus sp., root inhibition occured only at concentrations larger than 0.6 mM Al (Silva et al. 2004). In several soybean genotypes evaluated under 0.7 mM Al stress, root inhibition of the sensitive genotypes and tolerant genotypes were 46.5 and 19.6%, respectively (Sopandie et al. 2003). Referring to this experiment; the J. curcas IP3 was more sensitive to Al than M.

malabathricum.

The root elongation inhibition had high correlation with Al concentration in the J. curcas root tips, as had

been reported in Pisum sativum (Yamamoto et al. 2001), Picea abies (Nagy et al. 2004), and barley (Tamas et al.

2006). Accumulation of aluminum in J. curcas root occurred in the first cm of root apex, but did not occur in M. malabathricum. This meant that there was not a mechanism of Al transport to the leaf of J. curcas.

M. malabathricum can accumulate Al into the leaf by Al- citrate binding in the xylem (Watanabe & Osaki 2002). M.

malabathricum also secreted high density of mucilage which can chelate aluminum (Watanabe et al. 2008). The Al localization in the root’s first cm was relatively homogenous, with no visually significant differences in the Al content. Pineros et al. (2005) also reported that the Al content among the three discrete root sections analyzed (0-0.25, 0.25-0.5, and 0.5-1 cm) had no significant differences.

a b c d

e

-Al +Al

f

-Al +Al

-Al +Al

g h i

-Al +Al -Al +Al -Al +Al

Figure 2. Comparing of root staining between J. curcas roots with M. malabathricum under with and without Al stress. a. J. curcas root was stained with hematoxylin, b. Schiff’s Reagent, c. Evan’s Blue, d. transversal section of the roots stained with hematoxylin, e. Schiff’s Reagent, f. Evan’s Blue. As a comparison plant, g. M. malabathricum roots were also stained hematoxylin, h.

Schiff’s Reagent, i. Evan’s Blue.

(5)

Peroxidation lipid in plant tissues can be visualized with Schiff’s reagent by the development of pink dye (Yamamoto et al. 2001; Yin et al. 2010). By using Schiff’s reagent, the lipid peroxidation was known to spread homogenously in all root apex. In J.curcas, the seven day treatment with 0.8 mM Al has caused degradation of plasma membrane lipid throughout the root apex tissue, mainly in the epidermis and cortex. The type of membrane damage is a typical symptom under oxidative stress (Yin et al.

2010). Al triggered reactive oxygen species (Yamamoto et al. 2002; Jones et al. 2006), which induced peroxidation of membrane lipid and symplastic space of the cells (Yamamoto et al. 2001).

0 2 4 6 8 10 12 14 16 18 20

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

0 10 20 30 40 50 60 70 80

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

0 0.1 0.2 0.3 0.4 0.5 0.6

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

0 50 100 150 200 250 300

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

0 5 10 15 20 25

0.0 mM Al 0.2 mM Al 0.4 mM Al 0.8 mM Al Al treatments

Malate µmol/g FW

J. curcas M. malabathricum

a

b b

b

a

b b b

c

bc

ab

a

bc

ab

a

b

b

b

a

b

c

ab ab

a

a b

c d

e f

Figure 3. Malate concentration of J. curcas and M. malabathricum in leaf (a, b), root (c, d), and media (e, f) treated with different concentration of AlCl3, (pH 4) for 7 days. The error bars denote the SE values of the mean of three seedlings.

Degradation of plasma membrane, especially in the lipid structure, caused disturbing results in membrane permeability, so a specific dye for cell viability, Evan’s blue can cross the membrane into the cytoplasm.

Aluminum induced cell death is indicated by extensive blue dye found in all parts of the root apex tissue (Yamamoto et al. 2001). Al accumulation on the outer plasma membrane affects mitochondrial functions by an unknown signal transduction pathway or Al transported across the plasma membrane directly interfere with the mitochondrial functions (Yamamoto et al. 2002).

(6)

Aluminum stress affected organic acid metabolism in plant tissue (Ma et al. 2001). The malate content both in the J. curcas or M. malabathricum leaf was affected by Al treatments. A decrease of malate content in the leaf up to 60% has been reported for M. malabathricum (Watanabe

& Osaki 2001). In the root, the influence of Al stress on the increase of malate content in both plant species was significant. The ability of organic acids to chelate and render Al is well established, and it has been speculated for some time that Al-tolerant plant use organic acids to detoxify Al either internally or in the rhizosphere (Delhaize et al. 1993).

Ryan et al. (2001) emphasized on organic acid exudation as an important factor in the Al-tolerance mechanism. The malate content in J. curcas root reached peak when treated with 0.8 mM Al, while malate exudation in J. curcas reached the peak in the 0.4 mM Al treatment, and then decreased in the 0.8 mM Al treatments. It meant that J. curcas exuded organic acid in response to aluminum stress, but when the stress reached 0.8 mM, it caused damage to the system of transporter in the plasma membrane. This caused a decrease in the malate exudation to the media. Yamamoto et al. (2001) reported that the high Al accumulation in the apoplast region and the high affinity of aluminum ions for the negatively charged membrane plasma seemed to contribute to the damage of membrane plasma. The damaged membrane plasma of J. curcas roots occurred in the root tips tissue when exposed with 0.8 mM Al for 7 days (Figure 2f).

M. malabathricum roots has a different pattern compared to J. curcas regarding malate content and malate exudation. The malate content in the M. malabathricum roots reached the peak in the 0.4 mM Al treatment, and decreased in the 0.8 mM Al treatment, while the peak of malate exudation occurred in the 0.8 mM Al treatment.

The exudation of organic acids may be one mechanism of tolerance in addition to leaves accumulation. In the histological preparation of M. malabathricum root, there was no Al accumulation and damage of membrane plasma.

This occurrence was caused by the ability of M.

malabathricum to transport Al to the leaves (Watanabe

& Osaki 2002) and the ability of M. malabathricum to exude malate to chelate Al in the medium. M.

malabathricum has a transport system from the root to the leaf facilitated by citrate which is highly expressed in the xylem, and also is able to exude oxalate and citrate in high concentration from the root apex into the medium (Watanabe & Osaki 2002). The avoidance mechanisms of Al accumulation in the root apex is an importance point for Al tolerance, such as a transport system to the leaf and accumulation in the vacuola (Watanabe & Osaki 2002) or exudation of Al-carboxylate into the medium (Kochian et al. 2005). Pineros et al. (2005) reported that Aluminum resistance in maize cannot be solely explained by root organic acid exudation.

In conclusion, J. curcas used malate synthesis and malate exudation as one of its tolerance mechanism to aluminum. J. curcas root has a different pattern with M.

malabathricum in malate synthesis and malate exudations when treated with different Al concentrations. We categorized J. curcas acc IP3 as more sensitive to aluminum than M. malabathricum.

ACKNOWLEDGEMENT

This research was supported by the bilateral exchange Program, JSPS-PPGHE Joint Research Project 2010 entitled:

“Molecular adaptation of J. curcas to acid soil for reforestation of tropical wasteland” and Hibah Kompetensi (Competence Grant) Project entitled:

“Isolation and expression of genes in the frame of obtaining plants tolerant to acid and aluminum stresses”.

REFERENCES

Achary VMM, Jena S, Panda KK, Panda BB. 2008. Aluminum induced oxidative stress and DNA damage in root cells of Allium cepa L. Ecotox Envir Saf 70:300-310. http://dx.doi.org/

10.1016/j.ecoenv.2007.10.022

Cançado GMA, Loguercio LL, Martin PR, Parentoni SN, Paiva E, Borem A, Lopes MA. 1999. Hematoxylin staining as a phenotypic index for aluminum tolerance selection in tropical maize (Zea mays L.). Theor Appl Gen 99:747-754. http://dx.

doi.org/10.1007/s001220051293

De la Fuente JM, Ramirez-Rodriguez V, Cabrera-Ponce JL, Herrera- Estrella L. 1997. Aluminum tolerance in transgenic plants by alteration of citrate synthesis. Science 276:1566-1568. http:/

/dx.doi.org/10.1126/science.276.5318.1566

Delhaize E, Ryan PR, Hebb DM, Yamamoto Y, Sasaki T, Matsumoto H. 2004. Enginering high-level aluminum tolerance in barley with the ALMT1 gene. PNAS 19:15249- 15254. http://dx.doi.org/10.1073/pnas.0406258101 Delhaize E, Ryan PR, Randal PJ. 1993. Aluminum tolerance in

wheat (Triticum aestivum L.) II. Aluminum-stimulated excretion of malic acid from root apices. Plant Physiol 103:695-702.

Divacara BN, Upadyaya HD, Wani SP, Gowda CLL. 2010. Biology and genetic improvent of Jatropha curcas L: a review. Appl Energy 87:732-742. http://dx.doi.org/10.1016/j.apenergy.

2009.07.013

Hue NV, Craddock GR, Adam F. 1986. Effect of organic anions on aluminum toxicity in subsoil. Soil Sci Soc Am J 50:28-34.

http://dx.doi.org/10.2136/sssaj1986.036159950050000 10006x

Jones DL, Blancaflor EB, Kochian LV, Gilroy S. 2006. Spatial coordination of aluminum uptake, production of reactive species, callose production and wall rigidification in maize roots. Plant Cell Envir 26:1309-1318. http://dx.doi.org/10.

1111/j.1365-3040.2006.01509.x

Kang DJ, Ishi R. 2006. Formation of organic acid in the root apices of rice plants (Oriza sativa L.) grown in acidic nutrient solution containing aluminum. Plant Prod Sci 9:228-231.

http://dx.doi.org/10.1626/pps.9.228

Kochian LV, Pineros MA, Hoekenga OA. 2005. The physiology, genetics and molecular biology of plant aluminum resistance and toxicity. Plant Soil 274:175-195. http://dx.doi.org/10.

1007/s11104-004-1158-7

Koyama H, Kawamura A, Hara T, Takita E, Shibata D. 1999.

Over Expression of mitochondrial citrate synthase gene improves the growth of carrot cells in Al-Phosphate medium.

Plant Cell Physiol 40:482-488.

Ma JF. 2000. Role of organic acids in detoxification of aluminum in higher plant. Plant Cell Physiol 41:383-390.

Ma JF, Ryan PR, Delhaize E. 2001. Aluminum tolerance in plants and the complexing role of organic acids. TRENDS in Plant Sci 6:273-278. http://dx.doi.org/10.1016/S1360-1385(01) 01961-6

(7)

Ma JF, Shen R, Nagano S, Tanimoto E. 2004. Aluminum targets elongating cells by reducing cell wall extensibility in wheat roots. Plant Cell Physiol 45:583-589. http://dx.doi.org/10.

1093/pcp/pch060

Miyasaka SC, Buta JG, Howel RK, Foy CD. 1991. Mechanisms of aluminum tolerance in snapbean Plant Physiol 96:737-743.

http://dx.doi.org/10.1104/pp.96.3.737

Murashige T, Skoog F. 1962. A revised medium for rapid growth and bioassays with tobacco culture. Physiol Plant 15:473- 497. http://dx.doi.org/10.1111/j.1399-3054.1962.tb08052.x Nagy NE, Dalen LR, Jones DL, Swensen B, Fossdal CG, Eldhuset TD. 2004. Cytologycal an enzymatic responses to aluminum stress in root tips of Norway spruce seedlings. New Phytol 163:595-607. http://dx.doi.org/10.1111/j.1469-8137.2004.

01134.x

Osawa H, Kojima K. 2006. Citrate-realese- mediated aluminum resistance is coupled to the inducible expression of mitochondrial citrate synthase gene in Paraserianthes falcataria. Tree Physiol 26:565-574. http://dx.doi.org/10.1093/

treephys/26.5.565

Piñeros MA, Shaff JE, Manslank HS, Alves VMC, Kochian LC.

2005. Aluminum resistance in maize cannot be solely explained by root organic acid exudation. A comparative physiological study. Plant Physiol 137:231-241. http://dx.doi.org/10.1104/

pp.104.047357

Poschenrieder C, Gunsé B, Corrales I, Barceó J. 2008. A glance into aluminum toxicity and resistance in plants. Sci Total Envir 400:356-368. http://dx.doi.org/10.1016/j.scitotenv.

2008.06.003

Ragauskas AJ, William CK, Davison BH, Britovsek G, Cairney J, Eckert CA, Frederick Jr WJ, Hallett JP, Leak DJ, Liotta CL, Meilenz JR, Murphy R, Templer R, Tscaplinski T. 2006. The path forward for biofuels and biomaterials. Sci 311:484-489.

http://dx.doi.org/10.1126/science.1114736

Ryan PR, Delhaize E, Jones DL. 2001. Function and mechanism of organic anion exudation from plant root. Annu Rev Plant Physiol Plant Mol Biol 52:527-560. http://dx.doi.org/10.1146/

annurev.arplant.52.1.527

Ryan PR, Delhaize E, Randall PJ. 1995. Mallat efflux from root apices and tolerance to aluminum are highly correlated in wheat. Aust J Plant Physiol 22:531-536. http://dx.doi.org/

10.1071/PP9950531

Silva IR, Novais RF, Jham GN, Barros NF, Gebrim FO, Nunes FN, Neves JCL, Leite FP. 2004. Responses of eucalypt species to aluminum: the possible involvement of low molecular weight organic acids in the Al tolerance mechanism. Tree Physiol 24:1267-1277. http://dx.doi.org/10.1093/treephys/24.11.

1267

Silva S, Pinto-Carnide O, Martins-Lopes P, Matos M, Guedes- Pinto H, Santos C. 2010. Differential aluminum changes on nutrient accumulation and root differentiation in an Al sensitive vs tolerant wheat. Envir Exp Bot 68:91-98. http://

dx.doi.org/10.1016/j.envexpbot.2009.10.005

Sopandie D, Marzuki I, Jusuf M. 2003. Aluminum tolerance in Soybean: Protein profiles and accumulation of Al in root.

Hayati 10:30-33.

Tamas L, Budikova S, Simonovicova M, Huttova J, Siroka B, Mistrik I. 2006. Rapid and simple method for Al-toxicity analysis in emerging barley roots during germination. Biol Planta 50:87-93. http://dx.doi.org/10.1007/s10535-005- 0079-5

Watanabe T, Misaya S, Hiradate S, Osaki M. 2008. Caracterization of root mucilage from Melastoma malabathricum, with emphasis on its roles in aluminum accumulation. New Phytol 178:581-589. http://dx.doi.org/10.1111/j.1469-8137.2008.

02397.x

Watanabe T, Osaki M. 2001. Influence of aluminum and phosphorus on growth and xylem sap composition in Melastoma malabathricum L. Plant Soil 237:63-70. http://

dx.doi.org/10.1023/A:1013395814958

Watanabe T, Osaki M. 2002. Role of organic acids in aluminum accumulation and plant growth in Melastoma malabathricu.

Tree Physio 22:785-792. http://dx.doi.org/10.1093/treephys/

22.11.785

Yamamoto Y, Kobayashi Y, Devi SR, Rikiishi S, Matsumoto H.

2002. Aluminum toxicity is associated with mitochondrial dysfunction and the production of reactive oxygen species in plant cells. Plant Physiology 128:63-72. http://dx.doi.org/

10.1104/pp.010417

Yamamoto Y, Kobayasi Y, Matsumoto H. 2001. Lipid peroxidation is an early symptom triggered by aluminum, but not the primary cause of elongation inhibition in pea roots.

Plant Physiol 125:199-208. http://dx.doi.org/10.1104/pp.125.

1.199

Yin L, Mano J, Wang S, Tsuji W, Tanaka K. 2010. The involvement of lipid peroxide-derived aldehydes in aluminum toxicity of tobacco roots. Plant Physiol 152:1406-1417. http://dx.doi.

org/10.1104/pp.109.151449

Referensi

Dokumen terkait

a knowledge gained more meaningful and learning activities become more interesting, because knowledge is beneficial for him to better appreciate the environment, to better

2522 มาตรา 160 ตรี จากเดิม มาตรา 160 ตรี “ผู้ใดฝ่าฝืนมาตรา 43 2 ต้องระวางโทษจ าคุกไม่เกินหนึ่งปีหรือปรับตั้งแต่ห้าพันบาทถึง สองหมื่นบาท หรือทั้งจ าทั้งปรับ